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<br />214 <br /> <br />GREAT BASIN NATURALIST <br /> <br />[Volume 55 <br /> <br />Wildlife Refuge. This section of the river has <br />the lowest gradient of the entire Green River <br />system. Riparian vegetation consists of willow <br />and tamarix with occasional cottonwoods. We <br />collected monthly samples in the Ouray <br />National Wildlife Refuge (see also Fig. 2). In <br />addition to benthic samples, water chemistry <br />was determined for each habitat type on each <br />sample date (Table 1). Salinity and conductivity <br />were recorded with a YSI meter (Yellowstone <br />Instruments); turbidity was measured with a <br />nephelometer; and hardness, pH, and alkalini- <br />ty were determined with a Hach Kit (Hach <br />Chemical Corporation). Water chemistry was <br />recorded at three locations per sample area on <br />each sample date. At each site, a min-max ther- <br />mometer was placed near the benthos-water <br />interface at the time of sampling and left for <br />10 days. Substrate composition was estimated <br />visually. <br /> <br />River Channel <br /> <br />The river channel was sampled approximate- <br />ly 1.3 km north of the United States Fish and <br />Wildlife Service (USFWS) hatchery on the <br />Ouray National Wildlife Refuge. Sampling was <br />adjacent to a sand bar that decreased water <br />turbulence and prevented shifting sands. Water <br />chemistry values were relatively stable. Turbid- <br />ity was substantially higher during the August <br />sample. Substrate consisted mostly of sand with <br /> <br /> <br />Wyoming <br /> <br />Colorado <br /> <br />J----I <br /> <br />lOOKilometCfS <br /> <br />Fig, 1. Regional map showing the location of the Ouray <br />National Wildlife Refuge, <br /> <br />little silt and detritus. Water levels were too <br />high during June (peak flow) to allow sampling. <br /> <br />Ephemeral Side Channel <br /> <br />During high flows the Green River will <br />occupy various smaller channels that are dry <br />during low-flow intervals. We have named <br />such habitats "ephemeral side channels." The <br />ephemeral side channel studied was approxi- <br />mately 2.75 km south of the USFWS hatchery. <br />For most of the year water levels in the main <br />channel were below the level of the ephemeral <br />side channel. However, during peak flow, water <br />filtered through a wooded area and gathered <br />into the channel, which was 10 m wide and <br />500 m long. As the river level dropped, flow <br />slowed and eventually stopped. Because the <br />side channel dried up shortly after the July <br />sample, no August sample was taken. Most <br />notable of the water chemistry measurements <br />was the increase of salinity and alkalinity when <br />comparing June to July. Water temperature <br />also deviated more during July, Substrate con- <br />sisted mostly of firm silt and detritus with little <br />sand. Sediment deposition contributed little to <br />the site during our study, <br /> <br /> <br />j <br /> <br />Fig, 2, Local map of the Ouray National Wildlife <br />Refuge, Uintah County, UT, showing the location of sam- <br />pling sites, <br /> <br />:' <br /> <br />- <br />. <br /> <br />. <br />. <br />